Abstract

This study investigated the binding abilities of extracellular polymers produced by an environmentally isolated strain of Enterococcus hirae towards phytoestrogen endocrine disruptors—biochanin A, formonetin, genistein and daidzein. The extracellular biopolymer exhibited notable binding and removal for all four phytoestrogens, with a maximum removal of daidzein (87%) followed by genistein (72%) at a 1–1.5 mg/mL concentration. Adsorption proceeded rapidly at ambient temperature. The adsorption data fitted well with the Langmuir isotherm. Based on the adsorption energy, the biopolymer binding of phytoestrogens was inferred as daidzein > genistein > biochanin A > formononetin. Toxicity of the biopolymer (5–250 µg/mL) evaluated using RAW 264.7 cell lines indicated no significant (p < 0.05) changes in viability. In biopolymer-challenged Caenorhabditis elegans previously exposed to daidzein, complete protection to developmental toxicity, such as reduced egg-laying capacity, egg viability and progeny counts of the worm, was observed. The results of this study offer valuable insights into understanding the potential role of microbial extracellular biopolymers in binding and removal of phytoestrogens with sustainable technological implications in modulating the toxic effect of high levels of endocrine disruptors in the environment.

Highlights

  • IntroductionPublisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations

  • Since the extracellular biopolymer produced by E. hirae exhibited the highest phytoestrogen-binding capacity, this strain was selected for biopolymer production and further studies

  • The present study demonstrated the capabilities of extracellular polymers produced by E. hirae for binding and removing the phytoestrogens daidzein, biochanin

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Summary

Introduction

Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations. The presence of man-made and naturally occurring contaminants in aquatic ecosystems has received increased attention as human activities continue to introduce complex mixtures of contaminants into surface waters. Both agricultural practices and industrial discharges are key contributors of endocrine-disrupting materials. In areas where agricultural practices are intense, endocrine disruptors from plant sources or phytoestrogens are prevalent in surface water. Crop residues and wastes after harvest remain in fields for sufficiently long periods of time and subsequently start rotting after rainfall, and the leachate directly runs off into water bodies

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